Feebates – Modeling
DEVELOPMENT OF OPTIONS FOR A VEHICLE FEEBATE IN CANADA
4. MODELING OF FEEBATE OPTIONS
4.1 DESCRIPTION OF MODELS
separate models were used in this analysis:
- TransportCanada Variant of Greene et al. Vehicle Purchase Model.
This is a spreadsheet-based, nested multinomial logit,consumer choice model that estimates the effect of
feebates on consumer purchasing behaviour and manufacturer
investment in fuel economy technologies. Each individual
vehicle model is included (830 in total North American
market), as well as its purchase price and fuel economy.
The model solves for fuel economy changes that maximize
consumer surplus given a defined feebate. Consumer
surplus is maximized in response to the feebate “price”
by:
- shiftingvehicle demand towards more fuel-efficient carsand reducing overall vehicle demand
- inducingmanufacturers to maintain or improve market shareby improving fuel economy, and
- providingfuel savings to the consumer through lower overallfuel consumption.
Themodel produces aggregate national results for a
single future year (15 years in the future), representing
the new long-run equilibrium impact of the feebate.
Transport Canada modified the US model to use aggregated
2003 Canadian and US sales data, updated the technology
cost curves based on a 2005 literature review (necessary
to track manufacturer responses to the feebate),
and added redesign thresholds provided by EEA. (These
EEA redesign thresholds are used to determine if
sales are adequate in Canada to induce manufacturers
to make manufacturing investments that produce fuel
economy improvements.)
A key assumption in the model is how consumers respond
to the price signal introduced by the feebate. The
model used the following elasticity assumptions
to model the price response of consumers:
- -10@ market share of 15 percent within a class
- -5@ market share of 10 percent between classes
- -1.0for overall sales
Somelimitations of these assumptions are discussed below.
- NRCanVehicle Stock Model. This is a simple
representation of vehicle turnover and usage overa 15-year period. The model also incorporates the
technology redesign schedule provided by EEA for the
US Energy Information Administration in order to estimate
the timing of technology investments. Outputs include
the path of annual fuel savings and GHG emission reductions
leading up to the fifteenth year.
4.2 BASE CASE AND ASSUMPTIONSTo
isolate the effect of the feebate, a base case is assessed.
This case is generated by the model and based on allowing
consumer and manufacturer behaviour to evolve naturally
in response to the availability of cost saving-technology
with no feebate. The base case has not been calibrated
to NRCan’s reference case and it does not incorporate
macroeconomic or demographic factors. However, in evaluating
the incremental impact of feebates, these are not major
limitations.
key assumptions that remain constant for all scenarios
are:
- Asingle fuel-efficiency cost curve for each class (providedby EEA)
- 2000minimum threshold for redesign of import vehicles
- 20,000minimum threshold for redesign of domestic vehicles
- Vehiclelife of 15 years
- Averageyearly distance traveled of 23,500 km, declining 4percent per year
- 15percent adjustment of fuel consumption rating to approximateon-road conditions
- 23percent rebound effect (where decreased fuel costsinduce more driving, thus negating a portion of the
feebate gains)
- 10percent discount rate.
LIMITATIONS
all modeling exercises, the current one is a crude approximation
of reality designed to provide policy guidance. While
the model has limitations that we highlight below, it
is our view that the model can be used to inform policy.
Limitations include:
- Decisionbasis. In the real world, manufacturers
would redesign based on a number of complex considerationsand consumers would be driven by a variety of considerations
that are not easily represented by a simple elasticity
function. In this simulation, the model assumes that
manufacturers redesign their vehicles to maintain
market share and not to maximize profits. Similarly,
societal costs may be fairly represented by consumer
surplus changes, but it is not possible to estimate
the share of the burden that would fall on producers
and not be passed on to consumers.
- Airquality benefits. Important co-benefits
from reduced fuel consumption like improved air quality,a reduction in adverse health outcomes and the monetary
value of those outcomes are also not modeled.
- Valuationof fuel savings. A central assumption
of the model is that consumers undervalue fuel savings.A key limitation is that there is no data on the extent
to which this is true of Canadian consumers. As a
result, we use the same assumption as Greene et al.
(three years undiscounted) and we undertake a sensitivity
analysis by examining the effect of assuming that
consumers already fully value fuel savings. To the
extent that consumers do undervalue fuel savings,
a feebate would be justified on efficiency grounds
alone, with carbon mitigation benefits additive.
- Consumerelasticities. These values determine
the extent to which consumers respond to price signals.Greene et al. used short-run elasticities, which are
assumed to vary with make/model market shares, but
are not estimated by manufacturer or vehicle class.
Given the function used, classes with larger market
shares have smaller elasticities, whereas models with
small market shares have high elasticities (in some
cases, unrealistically high). Furthermore, cross-price
elasticities are not differentiated by make/model
or class. This means that consumers diverted from
buying a large SUV are assumed to be equally likely
to buy a subcompact as a minivan or mid-size SUV.
It also means that cross-price elasticities are higher
across the board for classes with large market shares;
this issue matters more for Canada, since the market
shares are less evenly distributed than in the US.
Since there is no comparable data on Canadian elasticities,
our approach has been to use the Greene et al. elasticities
but to halve them, as a way of approximating long-run
responses and to mitigate some of the effects described
above. We also undertake a sensitivity analysis by
examining the effects of assuming the full elasticities
prescribed by Greene et al.
- Staticdesigns. The model uses a database of
vehicles, which is based on 2003 models and assumesno changes in makes and models over the 15-year period.
This is unrealistic but neutral in terms of costs.
Furthermore the model uses a static technology cost
curve that assumes no progress in available fuel economy
technologies over the period—this assumption
tends to overestimate costs. Finally, the model assumes
that all technology investments are used to improve
fuel economy and that weight and performance remain
constant. (Given past experience, this tends to overestimate
the fuel economy effectiveness of the investments.)
- Hybridand diesel technologies are not included.
As discussed in Section 2, hybrids and diesels areexpected to play a significant role in improving fuel
economy. Unfortunately the current version of the
model lacks the information necessary to include these
options. (Our understanding is that Transport Canada
is working to add them to the model soon.) As a result,
the model overestimates costs and underestimates fuel
economy gains.
- Effectson used vehicle markets are not modeled.
As discussed in Section 2, the used vehicle marketrepresents more than half of vehicle sales. If the
price of certain models rises because of feebates,
it is likely that some of the demand will be filled
from the used vehicle market. However, the model assumes
that consumers primarily respond by shifting purchases
to other new vehicles. As a result, the effectiveness
of fuel economy gains is overestimated.
- Thresholdapproach to redesign. The cost curve
approach does not account for economies of scale beyondthe pre-set threshold, as the thresholds are only
set to limit the access to technology in a Canadian-only
scenario.
- Spillovereffects of unilateral Canadian policy.
The model assumes that unilateral Canadian policieshave no effect on US policy. Thus any spillover effects
that might occur are discounted. For example, should
Canadian policies increase the potential for voluntary
or mandatory fuel economy improvements in the US,
the effect of this on the overall size of the market
for redesign is not included. (As a result, costs
are potentially overestimated and effectiveness is
underestimated.)
- Reboundeffect. “Rebound” refers
to the increase in distance travelled that accompaniesreduced driving expenses (in this case, fuel savings).
The model assumes a rebound effect of 23 percent—meaning
23 percent of fuel savings are lost to this effect—based
on research of past experience in the US. The potential
future rebound effect in Canada has not been studied,
but 23 percent almost certainly overestimates the
effect and therefore underestimates the GHG savings.
SCENARIOS
primary purpose of the modeling is to explore the effects
of various feebate options. In this respect, the model
is primarily designed to examine the effects of varying
rate designs as opposed to implementation options, such
as approaches to revenue neutrality, phase-in periods,
or annual feebates at vehicle registration. As well,
the model is designed to use fuel consumption as the
rate basis.
our scenarios are selected to include variations on
the following options:
- Formof the function: Fully linear, $5,000 cap, or zerofeebate within 1.0 litre per 100 km of pivot (deadband)
- Rate:$250, 500, or $1000 per litre per 100 km
- Numberof classes: single, car and truck, or 11 classes.
secondary purpose of the modeling is to examine the
sensitivity of the results to differences in key assumptions.
In this respect, the following alternatives are considered:
- Elasticities
- Baseassumption – represents long-run elasticities(i.e. half of the values used by Greene et al.
presented above)
- -5@ market share of 1.5 percent within a class
- -2.5@ market share of 10 percent between classes
- -0.5for overall sales
- Sensitivityanalysis for double these figures (i.e. the fullvalues used by Greene et al.).
- Baseassumption – represents long-run elasticities(i.e. half of the values used by Greene et al.
- PolicyScope
- Baseassumption: feebates are implemented in Canadaonly
- Sensitivityanalysis for Canada–US policy.
- ConsumerPerception of Value of Fuel Savings
- Baseassumption: three years of undiscounted savings
- Sensitivityanalysis for fuel discounted valuation.
- FuelPrice
- Baseassumption: C$0.90 per litre
- Sensitivityanalysis at C$1.20 per litre.
alternative options and assumptions are grouped into
12 scenarios, as shown in Table 4.1.
|
No. |
Rate (C$/l/100km)
|
Classes |
Caps or Plateaus
|
Elasticities |
Jurisdictions |
Valuation of Fuel Savings
|
Fuel Price $/l
|
|---|---|---|---|---|---|---|---|
|
1 |
Base
Case |
N/A |
N/A |
50%
of Greene |
Canada
– US |
3
years, undiscounted |
0.90 |
|
2 |
$250 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
3 |
$500 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
4 |
$1,000 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
5 |
$500 |
Single |
No |
50%
of Greene |
Canada
– US |
3
years, undiscounted |
0.90 |
|
6 |
$500 |
Single |
Cap
at $5,000 |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
7 |
$500 |
Single |
Zero
within 1.0l/100km of pivot |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
8 |
$500 |
Separate
cars & trucks |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
9 |
$500 |
11
classes |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
10 |
$500 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
11 |
$500 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
0.90 |
|
12 |
$500 |
Single |
No |
50%
of Greene |
Canada
only |
3
years, undiscounted |
1.20 |
4.5
RESULTS
Appendix
B contains detailed result for each of the scenarios.
Selected results are presented in Table 4.2.
Note that Scenario 7 could not be modeled because
of problems with the specification of the discontinuity.
4.2: Scenario Results
|
Scenario
|
Total Transfer ($M)
|
Fuel Economy (l/100km) 2018
|
Unval. Fuel Savings ($M)
|
GHG Emission Reduction (Mt)
|
Societal Cost ($M)*Benefit shown as neg.
|
Sales (2010)
|
||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
# |
Policy
Options |
Assumptions |
2010 |
Cars |
Trucks |
2018 |
2018 |
2003-2018 |
2010 |
2018 |
2003-2018 |
Total
Change (#veh.) |
Big
3 (%) |
Other
(%) |
Cars
(%) |
Trucks
(%) |
Avg.
Car Price ($) |
Avg.
Truck Price ($) |
|
1 |
Base
Case |
First
3 yrs valuation Base Elasticities |
0 |
7.1 |
9.8 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
62 |
38 |
56 |
44 |
24,600 |
32,600 |
|
2 |
$250/l/100
km |
Canada
only First 3 yrs valuation Base Elasticities |
290 |
6.9 |
9.7 |
180 |
1.5 |
13 |
(80) |
(180) |
(540) |
(260) |
61 |
39 |
58 |
42 |
24,200 |
32,500 |
|
3 |
$500/l/100
km |
570 |
6.8 |
9.5 |
370 |
3.0 |
26 |
(120) |
(310) |
(800) |
(1,200) |
60 |
40 |
59 |
41 |
23,800 |
32,400 |
|
|
4 |
$1000/l/100
km |
1,100 |
6.5 |
9.2 |
760 |
6.2 |
53 |
(90) |
(460) |
(460) |
(6,300) |
58 |
42 |
62 |
38 |
23,100 |
32,200 |
|
|
5 |
$500/l/100
km |
North
America |
550 |
6.4 |
8.8 |
730 |
6.0 |
42 |
(160) |
(650) |
(1,340) |
(1,800) |
60 |
40 |
59 |
41 |
23,900 |
32,600 |
|
6 |
$500/l/100km
Cap@$5,000 |
Canada
only First 3 yrs valuation Base Elasticities |
570 |
6.8 |
9.5 |
370 |
3.0 |
26 |
(120) |
(310) |
(800) |
(1,200) |
60 |
40 |
59 |
41 |
23,800 |
32,400 |
|
8 |
$500/l/100km
Sep. Cars & Trucks |
450 |
6.8 |
9.5 |
250 |
2.1 |
16 |
(70) |
(220) |
(480) |
(860) |
61 |
39 |
56 |
44 |
23,800 |
31,400 |
|
|
9 |
$500/l/100km
11 Classes |
280 |
6.8 |
9.6 |
200 |
1.6 |
12 |
(50) |
(180) |
(380) |
(520) |
61 |
39 |
56 |
44 |
23,900 |
32,400 |
|
|
10 |
$500/l/100km |
Full
Valuation |
590 |
6.6 |
9.2 |
0 |
3.0 |
26 |
20 |
(20) |
292 |
(47)) |
61 |
39 |
58 |
42 |
23,700 |
32,500 |
|
11 |
$500/l/100km |
Double
Elasticities |
560 |
6.7 |
9.3 |
1,200 |
5.4 |
49 |
(540) |
(1,070) |
(3,540) |
(5,700) |
58 |
42 |
62 |
38 |
23,000 |
32,100 |
|
12 |
$500/l/100km |
$1.20/l |
580 |
6.7 |
9.4 |
400 |
2.4 |
21 |
(160) |
(360) |
(990) |
(30) |
60 |
40 |
59 |
41 |
23,700 |
32,400 |



















